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EPA's Vessel General Permit and Small Vessel General

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diets (Reich et al. 2010, V<strong>and</strong>er Z<strong>and</strong>en et al. 2010).<br />

Diving<br />

Loggerhead diving behavior varies based upon habitat, with longer surface stays in deeper<br />

habitats than in coastal ones. Routine dives can last 4–172 min (Byles 1988, Sakamoto et al.<br />

1990, Renaud <strong>and</strong> Carpenter 1994). The maximum-recorded dive depth for a post-nesting<br />

female was over 230 m, although most dives are far shallower (9-21 m (Sakamoto et al. 1990).<br />

Kemp’s ridley turtle (Lepidochelys kempii)<br />

Species description <strong>and</strong> distribution.<br />

The Kemp's ridley turtle is the smallest of all sea turtles. It was formerly known only from the<br />

Gulf of Mexico <strong>and</strong> along the Atlantic coast of the U.S. (TEWG 2000); however, there have<br />

been recent records of Kemp’s ridley turtles in the Mediterranean Sea (Tomas <strong>and</strong> Raga 2008).<br />

Status<br />

In 1970, the Kemp’s ridley turtle was listed as endangered under the ESA (35 FR 18319). The<br />

International Union for Conservation of Nature (IUCN) has classified the species as critically<br />

endangered. It was once considered the most endangered sea turtle (NRC 1990a, USFWS 1999).<br />

NMFS has not designated critical habitat for Kemp’s ridley sea turtle.<br />

Population designations, abundance, <strong>and</strong> trends<br />

Kemp’s ridley females lay their eggs in synchronized nesting events called aribadas. The species<br />

was once abundant in the Gulf of Mexico, with arribadas of 40,000 turtles at Rancho Nuevo,<br />

Mexico (Hildebr<strong>and</strong> 1963). By 1978, arribadas had declined to ~200 turtles (USFWS <strong>and</strong><br />

NMFS 1992, TEWG 2000). Protection led to increases in abundance in the early 1990s. By<br />

2006, there were approximately 7,866 nests at Rancho Nuevo <strong>and</strong> ~12,000 nests throughout<br />

Mexico which translates to an estimated 4,000 females nesting annually (Rostal et al. 1997,<br />

USFWS 2006, Rostal 2007) <strong>and</strong> a total population size of 7,000 – 8,000 adult females (Marquez<br />

et al. 1989, TEWG 2000, Rostal 2007). In Mexico, there were 17,882 nests in 2008 (Gladys<br />

Porter Zoo 2008) <strong>and</strong> 21,144 nests in 2009 (Gladys Porter Zoo 2010). In 2010, nesting declined<br />

to 13,302 nests (Gladys Porter Zoo 2010) but recovered to 20,570 nests in 2011<br />

(http://www.fws.gov/northflorida/SeaTurtles/Turtle%20Factsheets/kemps-ridley-sea-turtle.htm).<br />

A successful head-start program has resulted in the reestablishment of nesting at South Padre<br />

Isl<strong>and</strong>: in 2011, 199 turtles nested on Texan beaches<br />

(http://www.nps.gov/pais/naturescience/current-season.htm).<br />

Threats<br />

The primary cause for the mid-century decline in Kemp’s ridley turtles was overharvesting of<br />

turtles <strong>and</strong> eggs. This threat has subsided in recent years. Habitat destruction remains a concern<br />

in the form of bottom trawling <strong>and</strong> shoreline development. Finkbeiner et al. (2011a) estimated<br />

that at least 98,300 individuals are caught annually in U.S. Atlantic fisheries (resulting in at least<br />

2,700 mortalities). Kemp’s ridley turtles have among the highest levels of PCB <strong>and</strong> DDT (Pugh<br />

<strong>and</strong> Becker 2001). Oil can also be hazardous to Kemp’s ridley turtles, causing significant<br />

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